International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Vol XXXV, Part B7. Istanbul 2004
forest cover with different densities: 0, 25, 50, 70 and 100 %.
The used ozone concentrations were related to the following
zones: tropical (0.247 g.cm-2), subarctic summer (0.346
g.cm-2), average latitudes in winter (0.395 g.cm-2) and
subarctic in winter (0.48 g.cm-2). Furthermore, we used two
extreme values of ozone contents corresponding to 0.495
g.cm3 and 0.959 g.cm3. These concentrations were
programmed in the 6S code database. For each simulation, we
considered the three sensors and various forests cover
densities.
2.3 Spectral indices
Theoretically, the “ideal” vegetation index should be sensitive
to vegetation cover, insensitive to soil background (color,
brightness, moisture and roughness), independent of the
spatial and spectral resolutions of the sensors, little affected
by atmospheric and environment effects, does not saturate
rapidly, normalize the drift of the sensor radiometric
calibration, as well as solar illumination geometry and senor
viewing conditions (Jackson ef al, 1983; Bannari, 1996).
These effects intervene simultaneously during in situ
measurements and at the time of the satellite and/or airborne
images data acquisition. In the literature, more than fifty
vegetation indices (Bannari et al, 1995) were developed for
different applications and to correct some of these different
problems. In this study we retain only those that are
developed to minimize the soil and atmospheric effects.
The Normalized Difference Vegetation Index (NDVI)
developed by Rouse et al. (1974) is the most popular index
and the most used in various remote sensing applications.
This index has undergone several transformations to minimize
soil and atmospheric effects. By considering the bare soil line
parameters, slope and origin, Richardson and Wiegand (1977)
developed the Perpendicular Vegetation Index (PVI).
However, Huete (1988) demonstrated that there was a
contradiction between the NDVI and PVI indices in
describing the spectral behaviour of vegetation and soil
background. Consequently, he developed a new vegetation
index called the Soil Adjusted Vegetation Index (SAVI),
which is somewhat a compromise between ratio indices
(NDVI) and orthogonal indices (PVI). The originality of this
transformation lies in the establishment of a simple model,
which describes adequately the soil-vegetation system. In
order to reduce the soil color and brightness on the SAVI,
Baret et al. (1989) proposed a new version of this index: the
Transformed Soil Adjusted Vegetation Index (TSAVI). The
soil line parameters (slope and origin) are introduced into the
calculation of this index, which gives it a global character, i.e.
it requires the use of only one index for different applications
instead of using a determined index for each specific
application (Baret ef al., 1989). To improve the sensitivity of
SAVI to vegetation and to increase its potential to
discriminate the bare soil, Qi et al (1994) proposed a
modified version: the Modified Soil Adjusted Vegetation Index
(MSAVI). Rondeaux er al. (1996) adapted the TSAVI
especially for agricultural applications in a new version
named Optimized Soil Adjusted Vegetation Index (OSAVI).
The OSAVI is a particular case of the TSAVI when the slope
(a) and the origin (b) of soil line are equal to 1 and 0,
respectively
In order to correct atmospheric diffusion on the NDVI,
Kaufman and Tanré (1992) developed a new vegetation
802
index: the Atmospherically Resistant Vegetation Index
(ARVI). A self-correction process for the atmospheric effect
on the red channel accomplishes the resistance of this index to
atmospheric effects. The resistance degree of the ARVI to the
atmospheric variations depends on the accuracy of the
determination of the atmospheric self-correction coefficient.
Based on the 5S code, Kaufman and Tanré (1992) recommend
the unit value for self-correction coefficient (y ^ 1) allow a
better adjustment for most remote sensing applications; unless
the aeroso| model is known a priori. To correct the
atmospheric effects on the TSAVI, Bannari ef al. (1997) have
proposed the Transformed Soil Atmospherically Resistant
Vegetation Index (TSARVI). This transformation was based
on the substitution of the red channel by the red-blue channel
as suggested by Kaufman and Tanré (1992) and on the
calculation of the bare soil line parameters (slope and origin)
in the red-blue/NIR apparent spectral space. Developed
especially for AVHRR sensor by using only apparent
reflectances, the Global Environment Monitoring Index
(GEMI) is a non-linear index. The objective of the GEMI is
to evaluate and manage globally the environment without
being affected by the atmosphere (Pinty and Verstraete,
1992). For a combined correction of the atmospheric effects
and optical properties of soil background, Huete ef a/. (1996)
proposed a new version of SAVI named the Enhanced
Vegetation Index (EVI).
Theoretically, the values of the optimal vegetation index must
be between 0 and |, respectively, for bare soil and dense
vegetation cover. However, because of the disturbances and
the problems raised above, the perfect linearity is not obtained
by any vegetation index (Bannari ef a/., 2000). This problem
is partially caused by the high sensitivity to the chlorophyll
absorption in the red, which saturates very quickly (Huete et
al., 1999). In order to solve the linearity problem, Roujean
and Breon (1995) proposed the Renormalized Difference
Vegetation Index (RDVI). This index is a simple re-
normalization of the NDVI in order to have a very good linear
relationship to the surface biophysics parameters. As for the
Modified Simple Ratio (MSR), it is an improved version of the
RDVI for biophysical parameters extraction in boreal forest
environment (Chen, 1996). To solve the linearity problem and
to correct atmospheric effects, Gitelson ef al. (1996) proposed
the Green Atmospherically Resistant Vegetation Index
(GARI), which exploits apparent reflectance in the blue, red,
green, and near infrared channels.
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